A method for controlling the activity of an electrochemical device (11) comprising a bioanode (3) and a biocathode (6) immersed in an electrolyte (10A, 10C) containing microorganisms, the anode compartment (8) and cathode compartment (9) being separated by at least one membrane (14), optionally a reference electrode, a difference in potential being applied between the bioanode (3) and the biocathode (6), or between the bioanode and the reference electrode, characterised in that the operation of the device is governed by a dual control: —a priority control of the difference in potential between the bioanode and the biocathode, or between the bioanode and the reference electrode, between a minimum limit value allowing the development of an electroactive biofilm at the bioanode and a maximum limit value lower than the oxidation potential of said biofilm, and—a secondary control, when the first control is in place, optimising the Faradaic efficiency of the biocathode. A device allowing said method to be carried out.
|
1. A method for regulating the activity of an electrochemical device said device having an anode and a cathode that are submerged in an electrolyte placed in an anodic compartment and a cathodic compartment, respectively, these compartments being separated by at least one membrane or connected to each other by a salt bridge, the device optionally including a reference electrode,
said method comprising the steps of:
applying a potential difference between the anode and the cathode, or between the anode and the reference electrode;
wherein the electrolyte of the anodic compartment, and the electrolyte of the cathodic compartment contain microorganisms in suspension or in the form of one or more biofilms, the electrodes thus being called the bioanode and biocathode, respectively, and in that the operation of the device is controlled via a dual regulation including the further steps of:
a first regulation called the priority regulation, of the potential difference between the bioanode and the biocathode or between the bioanode and the reference electrode, between a minimal limit value allowing an electroactive biofilm to develop on the bioanode and a maximum limit value that is lower than the oxidation potential of said biofilm; and
once the first regulation has been implemented, a second regulation, called the subsidiary regulation, that optimizes the faradaic efficiency of the biocathode; and
wherein, while maintaining the first regulation of potential difference controlling the biological activity at the bioanode, the second regulation controls the optimization of the current density at the biocathode with a view to producing particular chemical species at the biocathode.
2. The method as claimed in
3. The method as claimed in
4. The method as claimed in
5. The method as claimed in
6. The method as claimed in
7. The method as claimed in
8. The method as claimed in
9. The method as claimed in
12. The method as claimed in
13. The method as claimed in
14. An electrolyzer for carrying out the method as claimed in
an anode and a cathode that are submerged in an electrolyte placed in an anodic compartment and a cathodic compartment, respectively, these compartments being separated by at least one membrane or connected to each other by a salt bridge, the electrolyte of the anodic compartment containing microorganisms, as does the electrolyte of the cathodic compartment, the electrodes thus being called the bioanode and biocathode, respectively;
optionally a reference electrode; and
means allowing a potential difference to be applied between the bioanode and the biocathode, or between the bioanode and the reference electrode, and means for controlling this potential difference;
wherein said electrochemical device comprises means allowing the faradaic efficiency of the biocathode to be optimized, the optimization being automatically controlled depending on physico-chemical parameters measured at the cathodic compartment and/or at the anodic compartment.
15. The electrochemical device as claimed in
16. The electrochemical device as claimed in
17. The method as claimed in
18. The method as claimed in
|
This application is a National Phase of PCT/FR2015/052585, filed on Sep. 29, 2015 which in turn claims the benefit of priority from French Patent Application No. 14 59281, filed on Sep. 30, 2014, the entirety of which are incorporated by reference.
Field of the Invention:
The present invention relates to the electrochemical field, and more particularly to electrochemical methods implementing bioelectrochemical devices, i.e. electrochemical devices, at least one of the electrodes of which makes contact with microorganisms.
Description of Related Art
Bioelectrochemical devices are recent. The study of biological anodes in the context of bio batteries started in the noughties in experimental devices in which the cathode was often abiotic. Sometimes, air cathodes that could optionally be biological were however used.
Bioelectrochemical devices have been subject to an increasing amount of attention over the last few years with a view to studying how to take advantage of and bioconvert organic material, which is in particular obtained from organic waste, in microbial electrolyzers. These bioelectrochemical devices require a biological anode (also called a bioanode) to be coupled to a biological cathode (also called a biocathode) and require a good kinetic coordination of the biological activities of the anode and cathode. Often, these activities are not well synchronized. Thus, the activity of one of the bioelectrodes in general takes precedence and may cause, in the circuit, potentials or currents that are detrimental to the correct operation of the other bioelectrode.
To the present day, biocathodes for electrosynthesis have practically never been studied in a system also including a bioanode. However, in future industrial waste biorefining applications, the use of both a bioanode and a biocathode will be necessary.
A first aim of the invention is therefore to mitigate the drawbacks of existing methods by making provision to regulate variations in the respective activities of the bioelectrodes, i.e. to coordinate the microbial activities both on a bioanode and on a biocathode of an electrochemical device, the anodic and cathodic compartments of which contain microorganisms.
To this end, the present invention proposes a method for regulating the activity of an electrochemical device including an anode and a cathode that are submerged in an electrolyte placed in an anodic compartment and a cathodic compartment, respectively, these compartments being separated by at least one membrane or connected to each other by a salt bridge, the device optionally including a reference electrode, a potential difference being applied between the anode and the cathode, or between the anode and the reference electrode; characterized in that the electrolyte of the anodic compartment, and the electrolyte of the cathodic compartment contain microorganisms in suspension or in the form of one or more biofilms, the electrodes thus being called the bioanode and biocathode, respectively, and in that the operation of the device is controlled via a dual regulation:
Conventionally, in microbial electrosynthesis experiments, since the reduction reactions take place on the biocathodes, prior-art electrochemical devices have merely implemented a regulation of the current or of the potential at the cathode. When a bioanode is present, this type of regulation may lead to a large increase in the potential at the anode, which leads to excessive oxidation and thus inactivation of the electroactive biomass on contact with this electrode.
Now, the inventors have observed that it is surprisingly and unexpectedly preferable to employ, on start, a strategy for regulating the potential at the anode. Once an oxidation microbial activity has been achieved at the anode such that a current level that is judged to be sufficient is obtained in the circuit, it becomes necessary to regulate the current density and/or the potential at the biocathode in order to allow a suitable biological activity at the cathode (regulation of the current or the potential in ranges compatible with the activity of the anode). The method according to the invention therefore first takes into account the variation in the biological activity at the anode, via the priority regulation of the potential at the bioanode (priority law).
Throughout the present document, the expressions coulombic efficiency, coulombic yield, faradaic yield and faradaic efficiency are equivalent and have the same meaning from the electrochemical point of view.
The current density (in A/m2) at the bioanode or at the biocathode corresponds to the current per unit area of the electrode of which it is question.
By “bioanode” and “biocathode” what is meant here is electrodes that are submerged in an electrolyte in contact with microorganisms and an electrolyte. These microorganisms may be organized into biofilms in direct contact with the electrodes, walls of the reactor and/or be in suspension in the electrolyte. Throughout the text the terms anode or bioanode, and cathode or biocathode will be used interchangeably.
Advantageously, while maintaining the regulation of the potential at the bioanode, the optimization of the activity of the biocathode with a view to producing particular chemical species is automatically controlled depending on physico-chemical parameters measured in the cathodic compartment, i.e. parameters such as the concentration of one or more chemical species in the electrolyte or in the gaseous atmosphere nearby the biocathode, or the rate of gas production at the biocathode.
The chemical species measured in the cathodic compartment is for example dihydrogen (resulting from an abiotic effect of electrolysis of water and meaning that the current must be decreased to improve the operation of the biocathode) or methane (which means that electro-methanogensis is occurring at the biocathode).
According to one advantageous embodiment of the invention, while maintaining the first regulation of potential difference controlling the biological activity at the bioanode, the second regulation controls the optimization of the current density at the biocathode with a view to producing particular chemical species at the biocathode.
This optimization of current density of the biocathode may be achieved:
In this second variant, the ratio of the active area of the bioanode to the active area of the biocathode may be varied:
In the case where the anodic and cathodic compartments comprise a plurality of electrodes (bioanodes or biocathodes, respectively), these electrodes are of course all connected to the same electrical circuit of the electrochemical device.
According to another embodiment, the activity of the biocathode may be regulated using physico-chemical parameters at the anodic compartment. More particularly, while maintaining the regulation of the potential at the bioanode, the activity of the biocathode is then optimized with a view to producing particular chemical species by regulating chemical parameters at the anodic compartment, i.e. parameters such as the concentration of one or more chemical species in the electrolyte or in the gaseous atmosphere nearby the bioanode.
This chemical species is advantageously a non-fermentable molecule such as an organic acid or its salt and is preferably chosen from acetate, lactate or propionate.
By way of exemplary priority regulation, when the bioanode, such as an electrode made of carbon, is submerged in an aqueous electrolyte having a pH of about 7, the maximum value of the potential difference between the bioanode and a standard hydrogen electrode, called reference electrode, is such that the potential of the bioanode is lower than or equal to 1 V with respect to said reference electrode and preferably lower than 0.5 V with respect to said reference electrode so as to prevent electrolysis of the water.
The present invention also relates to an electrochemical device for carrying out the method described above, allowing currents and/or potentials at the cathode to be controlled depending on the variation in the biological activity at the anode.
More specifically, the electrochemical device according to the invention comprising:
The membrane may be an ion exchange membrane: cation exchange membrane, anion exchange membrane, proton exchange membrane; or as a variant may be an osmosis membrane.
This electrochemical device may also comprise sensors or probes placed in the electrolyte and/or in the gaseous atmosphere nearby the bioanode or biocathode, respectively, said sensors or probes measuring physico-chemical parameters at the anodic compartment and/or the cathodic compartment, i.e. parameters such as the concentration of one or more chemical species.
The electrochemical device according to the invention may also comprise means allowing the level of the electrolyte in at least one of the compartments to be varied (for example by means of a pump connected to an inlet and an outlet of the corresponding compartment) and/or allowing the bioanode and/or the biocathode to be moved in the electrolyte.
The invention will be better understood on reading the following description of exemplary embodiments, given with reference to the appended drawings, in which:
The electrochemical device 1 shown in
The bioanode was “precultivated” on acetic acid in biological sludge, this allowing a biofilm containing electroactive bacteria to be obtained on the surface of the carbon fabric. The cathodic compartment 9 may optionally be inoculated with an acetogenic bacteria culture prepared from an anaerobic waste-processing microbial consortium (biocathode).
The anode 3 is initially polarized to +0.158 V with respect to a saturated calomel reference electrode 7 (SCE) by means of a potentiostat (Biologic®, France, VMP3, software package EC-Lab) (priority law). When the current density reaches 5 A/m2, the potentiostat is programmed to limit the current density to this value. This allows the activity of the cathode to be regulated (subsidiary law). Lastly, if the potential at the anode exceeds +0.2 V versus SCE, the potentiostat is then set up to switch back to the potential control mode and to maintain this value in order to preserve the biological activity of the bioanode (priority law). This regulation is illustrated in
Throughout the experiment, samples are taken in which concentrations of volatile fatty acids and lactate are measured by ion chromatography (DIONEX DX 120, IONPAC® ICE-AS1 column (9×250 mm)). The eluents used are heptafluorobutyric acid (0.4 mmol/L) and tetrabutylammonium hydroxide (TBAOH, 5 mmol/L). The concentrations of formate, acetate, lactate, propionate, butyrate and valerate are thus measured in a range extending from 10 mg/L to 500 mg/L. The compositions of the gaseous atmospheres of the anodic and cathodic compartments are measured by gas phase chromatography (Varian CP 4900). The three columns of the instrument allow the proportions of the following gases to be measured: O2, N2, CH4, CO2, H2, H2S and NO2.
The experiment was carried out for 30 days, with two injections of substrate into the anodic compartment 8 (600 mg/L of acetic acid) on days 0 and 15. Three pilots were launched in parallel under the same conditions with inoculation at the cathode (biocathode) and three other control pilots were launched without inoculation at the cathode. The behaviors of the three pilots with inoculation turned out to be very similar throughout the experiment, one thereof was stopped on day 15 to allow observation of the electrodes by microscopy. The production tally of the biocathode of one of these pilots is shown in
During the first phase of the experiment (days 1 to 15), hydrogen (H2) and methane (CH4) are mainly produced in the cathodic compartments having received an inoculation whereas the pilots without inoculation of the cathodic compartment produce only hydrogen. The faradaic efficiency at the biocathode is then 60% with 53% of the electrons used to produce methane (
On day 15, the second substrate is injected into the anodic compartment 8 and 10 mmol/L of 2-bromo-ethane sulfonate (BES) are injected into the cathodic compartment 9 to inhibit methanogenesis. During the second phase, volatile fatty acids such as formate and acetate are mainly produced, as well as small amounts of hydrogen and methane. The faradaic efficiency at the cathode then reaches 80%. 29% of the electrons have been used to produce acetate. The maximum rate of production of acetate recorded during this phase is 11 g of acetate/m2/day. Moreover 18%, 19% and 13% of the electrons are used to produce formate, hydrogen and methane respectively (
The faradaic efficiency at the anode during the experiment is 85% on average.
Observations of the bioanodes and biocathodes under confocal laser scanning microscope at 15 days and 30 days reveal a substantial microbial colonization of the two bioelectrodes.
Optimization of the current at the biocathode by regulation of potential difference.
In this exemplary embodiment, the bioelectrochemical reactor is a dual-compartment electrolyzer such as that shown in
More particularly, in the first phase of the experiment, the potential difference is set to 0.9 V between the bioanode and the biocathode. After about one day of experiment, the potential difference is increased to 1.4 V between the two electrodes. The obtained curve of current as a function of time confirms that this variation in potential difference causes an increase in current, from about 5-6 mA to 15 mA. After 4 days, the potential difference is returned to 0.9 V and is correlated with a drop in the current to a value very close to its initial value (about 5 mA). Controlling the potential difference between the bioanode and biocathode therefore allows the magnitude of the current flowing through the bioelectrochemical reactor to be regulated and therefore the activity of the biocathode to be regulated.
Optimization of the current at the biocathode by movement of the bioanode in the electrolyte.
In this exemplary embodiment, the bioelectrochemical reactor is a dual-compartment electrolyzer such as that shown in
Specifically, in this exemplary embodiment, the submerged area of the bioanode is modified a plurality of times during the experiment. After a little more than one day, half of the bioanode 3 is raised out of the electrolyte, decreasing the submerged area by half. In parallel to this, a decrease in the current from 8 mA to about 5 mA is observed. On the second day, the bioanode is again completely submerged in the electrolyte and then an abrupt increase in the current is observed. The experiment is thus repeated 3 times and allows, on each variation in the submerged area of the bioanode, a correlated variation in the current at the biocathode to be observed. Controlling the submerged area of the bioanode therefore allows the current of the bioelectrochemical reactor to be regulated and therefore the activity of the biocathode to be regulated.
Regulation of the current at the biocathode depending on concentration in COD (chemical oxygen demand) at the anode.
In this exemplary embodiment, the bioelectrochemical reactor is a dual-compartment electrolyzer such as that shown in detail in
TABLE 1
Conc. (g/L)
Lactic acid
10.52
Formic acid
0.00
Acetic acid
0.38
Propionic acid
1.28
Butyric acid
5.32
Valeric acid
0.00
The least supplied reactor received 31.5 mg/L/d of COD on average and the second 94.5 mg/L/d of COD on average. This difference in substrate concentration allowed a different current to be obtained for each reactor since the average current obtained for the reactor supplied with 1 mL of substrate was 1.1 mA, whereas the average current obtained for the reactor supplied with 3 mL of substrate was 4.3 mA (
Optimization of the activity of the biocathode by regulation of chemical parameters.
This example implements an electrochemical device including physico-chemical sensors. This electrochemical device 11, which is shown schematically in
Various sensors or probes may be integrated into the two compartments in order to follow the variation in physico-chemical parameters of the system: for example, a gas sensor 13 is placed in the gaseous atmosphere 12 of the anodic compartment and a probe 18 is submerged in the liquid electrolyte 10A of the anodic compartment 8. Likewise, a gas sensor 16 is placed in the gaseous atmosphere 15 of the cathodic compartment and a probe 19 is submerged in the electrolyte 10C of the cathodic compartment 9.
While maintaining the regulation of the potential at the bioanode, the activity of the biocathode is optimized by regulating chemical parameters of the anodic compartment 8, i.e. parameters such as the concentration of one or more chemical species in the electrolyte 10A or in the gaseous atmosphere 12 nearby the bioanode, pH, etc. The presence of various integrated sensors/probes in the two compartments allows the variation in the physico-chemical parameters of the system to be followed directly. Depending on the value of these parameters, the electronic device 17 may then optimize the operation of the biocathode by adjusting the current of the system, the electrical potential, etc.
In this exemplary embodiment, the electrochemical device 21 is a dual-compartment electrolyzer including a bioanode 22 and a biocathode 35 that are formed from graphite granules 20 connected to the exterior electric circuit by graphite rods. The anodic and cathodic compartments 28, 39 are separated by a cation exchange membrane 24 (CEM). The anodic compartment 28 includes an inlet 23 and an outlet 25 for the electrolyte 10A, which inlet and outlet are for example connected to pumping means (not shown). Likewise, the cathodic compartment 39 includes an inlet 30 and an outlet 31 for the electrolyte 10C, which inlet and outlet may be connected to pumping means (not shown) that are independent from the pumping means connected to the anodic compartment.
This device allows the level 26 of the electrolyte 10 in the anodic compartment and the level 36 of the electrolyte 10C in the cathodic compartment, and therefore the volume of electrolyte in each of these compartments, to be independently modulated, and thus the ratio of the active (i.e. submerged) areas of the two bioelectrodes to be controlled.
In the case where the current (I) is set, this modulation allows the potential difference (E) between the two bioelectrodes to be varied. This makes it possible, initially, during the start-up of the system, to obtain a potential at the anode that is compatible with the instigation of electroactive biological activity. Subsequently, this allows the biosynthesis reactions at the cathode to be controlled, regulating its potential.
In the case where the potential difference (E) between the two bioelectrodes is set, this regulating system allows the electrical current (I) to be modulated, and this will have a direct influence on the carbonic production efficiencies of various molecules, allowing the efficiencies of conversion of electrons into molecules of interest to be optimized.
Optimization of current by regulation of potential difference (ΔE) in a dual-compartment electrolyzer including electrodes formed from graphite granules.
In this exemplary embodiment, the electrochemical device 21 is a dual-compartment electrolyzer such as that shown in
The embodiment of the method of the present invention here consists in modulating the potential difference between the anode 22 and the cathode 35 by virtue of the use of a potentiostat to control current.
Controlling the potential difference between the bioanode and biocathode therefore allows the magnitude of the current flowing through the dual-compartment bioelectrochemical reactor including electrodes formed from graphite granules to be regulated and therefore the activity of the biocathode to be regulated.
In this exemplary embodiment, the electrochemical device, schematically shown in
According to this embodiment, the anodic compartment of a reactor has been continuously supplied with biodegradable waste (from the substrate composition presented in table 1 of example 4) by virtue of a pump allowing the flow rate entering to be regulated, and of an overflow system allowing a constant level of liquid to be preserved within the anodic compartment maintained at a volume of 1 L.
The impact of various substrate concentrations in the supply (COD load, COD standing for chemical oxygen demand) on the current has been tested for an average flow rate of 82 mL/day over an average duration of 10 days. The results are shown in
The observed correlation between the magnitude of the current in the circuit and the flow rate of supplied COD clearly shows that regulation of the flow rate of supplied substrate allows the magnitude of the current to be regulated.
Bouchez, Théodore, Bridier, Arnaud, Le Quemener, Elie
Patent | Priority | Assignee | Title |
11862394, | Jan 16 2019 | Durham University | Electrochemical capacitor device with a biofilm |
Patent | Priority | Assignee | Title |
4652501, | Jul 24 1984 | KING S COLLEGE LONDON | Operation of microbial fuel cells |
20060234110, | |||
CN102925492, | |||
WO2009008709, |
Date | Maintenance Fee Events |
Nov 25 2022 | M1551: Payment of Maintenance Fee, 4th Year, Large Entity. |
Date | Maintenance Schedule |
Jun 25 2022 | 4 years fee payment window open |
Dec 25 2022 | 6 months grace period start (w surcharge) |
Jun 25 2023 | patent expiry (for year 4) |
Jun 25 2025 | 2 years to revive unintentionally abandoned end. (for year 4) |
Jun 25 2026 | 8 years fee payment window open |
Dec 25 2026 | 6 months grace period start (w surcharge) |
Jun 25 2027 | patent expiry (for year 8) |
Jun 25 2029 | 2 years to revive unintentionally abandoned end. (for year 8) |
Jun 25 2030 | 12 years fee payment window open |
Dec 25 2030 | 6 months grace period start (w surcharge) |
Jun 25 2031 | patent expiry (for year 12) |
Jun 25 2033 | 2 years to revive unintentionally abandoned end. (for year 12) |